Abstract
Dynamic N-mixture models have been recently developed to estimate demographic parameters of unmarked individuals while accounting for imperfect detection. We propose an application of the Dail and Madsen (2011: Biometrics, 67, 577–587) dynamic N-mixture model in a manipulative experiment using a before-after control-impact design (BACI). Specifically, we tested the hypothesis of cavity limitation of a cavity specialist species, the northern flying squirrel, using nest box supplementation on half of 56 trapping sites. Our main purpose was to evaluate the impact of an increase in cavity availability on flying squirrel population dynamics in deciduous stands in northwestern Québec with the dynamic N-mixture model. We compared abundance estimates from this recent approach with those from classic capture–mark–recapture models and generalized linear models. We compared apparent survival estimates with those from Cormack–Jolly–Seber (CJS) models. Average recruitment rate was 6 individuals per site after 4 years. Nevertheless, we found no effect of cavity supplementation on apparent survival and recruitment rates of flying squirrels. Contrary to our expectations, initial abundance was not affected by conifer basal area (food availability) and was negatively affected by snag basal area (cavity availability). Northern flying squirrel population dynamics are not influenced by cavity availability at our deciduous sites. Consequently, we suggest that this species should not be considered an indicator of old forest attributes in our study area, especially in view of apparent wide population fluctuations across years. Abundance estimates from N-mixture models were similar to those from capture–mark–recapture models, although the latter had greater precision. Generalized linear mixed models produced lower abundance estimates, but revealed the same relationship between abundance and snag basal area. Apparent survival estimates from N-mixture models were higher and less precise than those from CJS models. However, N-mixture models can be particularly useful to evaluate management effects on animal populations, especially for species that are difficult to detect in situations where individuals cannot be uniquely identified. They also allow investigating the effects of covariates at the site level, when low recapture rates would require restricting classic CMR analyses to a subset of sites with the most captures.
Highlights
Understanding how environmental variables affect spatial or temporal variation in species abundance is one of the main goals of ecological research
Ecology and Evolution published by John Wiley & Sons Ltd
We examine the value of dynamic N-mixture models for understanding the population dynamics of the northern flying squirrel (Glaucomys sabrinus), which is of particular interest in North American forest management
Summary
Understanding how environmental variables affect spatial or temporal variation in species abundance is one of the main goals of ecological research. Developed analytical approaches enable the estimation of demographic parameters from unmarked individuals (Royle 2004; Dail and Madsen 2011). Such models use count data collected at a number of visits in a given season from a suite of sites, in order to follow temporal variations in population size. These methods show promise in ecology, wildlife management and conservation biology, especially when a limited number of individuals are captured at several sampling sites
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